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Helserisiko ved PCB

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Complex mixture of some 150 (of a total of 209) different congeners. ... Dioxins and coplanar PCB in Guillemot. ng TEQ/g fat. TEQ, toxic equivalency ... – PowerPoint PPT presentation

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Title: Helserisiko ved PCB


1
Helserisiko ved PCB
  • Niklas Johansson
  • Karolinska institutet
  • och Naturvårdsverket

2
What is PCB?
  • Complex mixture of some 150 (of a total of 209)
    different congeners.
  • These are resistant to break down
  • Chemically related but show profound biological
    differences

3
PCB 209 different congeners
orto-
Cl
para-
Cl
meta-
Cl
4
The PCB story in Sweden
  • 1966 Identified in the environment
  • 1971 First legislation on PCB
  • 1973 Use in open applications banned
  • 1978 New use in closed applications


    banned
  • 1988 Step wise reduction of use in closed
    systems
  • 1995 All use banned

5
PCB some important properties
  • Resist high pressure and temperature
  • Good electric inulator
  • Not flammable at low temperatures
  • Good stabilizing properties for polymers
  • Resist biological and chemical degradation
    processes, but
  • Can be bio-accumulated and bio-magnified and
    cauce severe chronic effects

6
Consequences of high persistancy
  • Will be present in the environment for decades or
    more
  • Could be distributed not only locally but on a
    broad scale
  • Eventually accumulated in certain compartments in
    the environment
  • Exposure times will be long
  • Actions and regulations will only slowly improve
    the environmental situation

7
PCB-level in soil at different distances from the
building
mg/kg
Distance from facade (m)
8
Dioxins and coplanar PCB in Guillemot
ng TEQ/g fat
9
TEQ, toxic equivalency
  • Some PCB (co-planar) act via the same mechanism
    as dioxins
  • Their toxicity is however generally lover
    compared to dioxins
  • By comparing the toxicity of different dioxins
    and PCBs with the most toxic dioxin, TCDD, a
    toxic equivalency factor, TEF, can be calculated
    for individual PCB and dioxin congeners
  • Total dioxin toxicity (TEQ) can be calculated

10
POPs in food, ng/kg b.w. and day
pg TEQ/kg b.w.and day
Vår föda, 2002, no 4
11
PCB in different foodstuffs
12
PCB in fish and shellfish in a normal diet
13
Dioxins and PCB in fish from the Baltic proper,
pg/g fresh weight (1995)
Currnet EU-limit for fish 4 pg/g fresh weight
(contains so far dioxins only)
14
Mean intake of dioxins and dioxin-like PCB
pg TEQ
Dayly intake 90-110 pg 1,3 pg/kg
b.w.
15
Dioxins and PCB in breast milk Mixed samples from
Stockholm
TEQ pg/g fat
16
Effects of PCB
  • Low acute toxicity
  • Skin
  • Digestive system
  • Lungs
  • Nervous system
  • Vitamin A homeostasis
  • Effects on the liver
  • Enzyme induktion
  • Affect the immune system
  • Reproductive disturbances
  • aborts
  • number of litters
  • Behaviour effects
  • Endocrine effects
  • Cancer
  • Etc. etc.

17
How toxic isPCB?
  • Some PCB show profound similarities with dioxins
    but they are less toxic than the dioxins.
  • Other PCB act via different mechanisms (Reports
    on mental retardation in children from USA, is
    attributed the non dioxin-like PCB)

18
Health risk assessment
  • Based on dioxin-like effects only
  • Tolerable Dayly Intake (TDI) of dioxins and
    dioxin-lika PCB 2 pg TEQ/kg b.w. (SCF, EU)
  • TDI often exceeded in the general population,
    especially by breast fed children but also by
    fishermen and their families

19
Livsmedelsverkets råd om konsumtion av fet fisk
20
Livsmedelsverkets råd om konsumtion av fet fisk
21
Conclusions
  • Human exposure has decreased since 1970 but
    exposure is still unsatisfactory high
  • Risk assessment based on dioxin-like effects only
  • TDI is exceeded in segments of the general
    population
  • Dietary recommendations still justified
  • Urgent to stop further PCB leakage into the
    environment

22
Is it dangerous to live in a PCB-house?
  • We know that the levels in air could be
    substantially elevated
  • Long exposure times
  • Low chlorinated PCB
  • Uptake probably high
  • Few human studies on the relationship between
    exposure via indoor air and levels in blood
  • Divergent results
  • No panic

23
Is it dangerous to live in a PCB-house?
  • En studie av sambandet mellan PCB-halt i
    inomhusluft och och halt i blod startad
  • Förstudie
  • mätning av halt i luft visar tydliga skillnader
  • Upp till 100 gånger högre totalhalter
  • Medelvärden 0,005 0,35µg/m3
  • Halterna dock väsentligt lägre än gränsvärde för
    arbetsmiljö (10 µg/m3)
  • Lågklorerade PCBer

24
PCB in Indoor and Outdoor Air (Relative Units)
25
Loading plot of the second (p2) and third (p3)
principal components
26
Is it dangerous to live in a PCB-house?
  • Huvudstudie
  • enkät för registrering av faktorer som kan
    påverka PCB-halt
  • mätning av PCB-halt i blod
  • Preliminära resultat pekar på att även halter i
    blod kan vara förhöjda
  • Ingen säker skillnad för dioxinlika PCBer (med
    TEF)

27
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28
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29
PCB levels in blood of residents (ng/g lipid)
30
But
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